U.S. patent application number 17/032076 was filed with the patent office on 2021-02-04 for air treatment system, method and apparatus.
The applicant listed for this patent is Novaerus Patents Limited. Invention is credited to Felipe Soberon.
Application Number | 20210033293 17/032076 |
Document ID | / |
Family ID | 1000005153625 |
Filed Date | 2021-02-04 |
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United States Patent
Application |
20210033293 |
Kind Code |
A1 |
Soberon; Felipe |
February 4, 2021 |
AIR TREATMENT SYSTEM, METHOD AND APPARATUS
Abstract
An air treatment apparatus, system and method for removal of
health threatening airborne pollutants from an airflow is provided.
The air treatment apparatus includes a ducting section having an
inactivation zone created by either a plasma-generating flexible
electrode alone, a UV light source alone, or a combination of a
plasma-generating flexible electrode and a UV light source disposed
within the interior of the ducting section, wherein the airflow and
airborne pollutants are urged into the inactivation zone ensuring
multiple exposures of airborne pollutant material into the
inactivation zone resulting in purified air exiting from the
apparatus.
Inventors: |
Soberon; Felipe; (Blackrock,
IE) |
|
Applicant: |
Name |
City |
State |
Country |
Type |
Novaerus Patents Limited |
Blackrock |
|
IE |
|
|
Family ID: |
1000005153625 |
Appl. No.: |
17/032076 |
Filed: |
September 25, 2020 |
Related U.S. Patent Documents
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Application
Number |
Filing Date |
Patent Number |
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15503211 |
Feb 10, 2017 |
10786593 |
|
|
PCT/EP2015/068605 |
Aug 12, 2015 |
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17032076 |
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Current U.S.
Class: |
1/1 |
Current CPC
Class: |
B01D 2259/818 20130101;
A61L 9/20 20130101; B01D 2259/804 20130101; F24F 8/22 20210101;
B01D 53/32 20130101; A61L 9/22 20130101; F24F 8/192 20210101; B01D
53/007 20130101 |
International
Class: |
F24F 3/16 20060101
F24F003/16; B01D 53/00 20060101 B01D053/00; B01D 53/32 20060101
B01D053/32; A61L 9/20 20060101 A61L009/20; A61L 9/22 20060101
A61L009/22 |
Foreign Application Data
Date |
Code |
Application Number |
Aug 12, 2014 |
GB |
1414244.2 |
Claims
1. An air treatment apparatus for removal of health threatening
airborne pollutants from an airflow, the air treatment apparatus
comprising: a ducting section defining an interior; an air inlet
port in a top of the ducting section for entry of airflow into the
apparatus; an exit port in a bottom of the ducting section and
opposing the air inlet port a plasma-generating flexible electrode
disposed within the interior and about an inner wall surface of the
ducting section creating an inactivation zone through a length of
the ducting section, wherein the airflow and airborne pollutants
are urged into the inactivation zone as the airflow travels in an
inward circular direction through the ducting section toward the
bottom of the ducting section and the exit port to ensure multiple
exposures of airborne pollutant material into the inactivation zone
as purified air exits through the exit port.
2. The air treatment apparatus as claimed in claim 1, wherein the
ducting section has a cylindrical shape.
3. The air treatment apparatus as claimed in claim 1, wherein the
apparatus further comprises an ultraviolet light source disposed
within the interior of the ducting section.
4. The air treatment apparatus as claimed in claim 3, wherein the
ultraviolet light source is positioned opposing the
plasma-generating flexible electrode within the interior of the
ducting section.
5. The air treatment apparatus as claimed in claim 3, wherein the
ultraviolet light source is disposed vertically within the interior
of the ducting section.
6. The air treatment apparatus as claimed in claim 3, wherein the
ultraviolet light source and the plasma-generating flexible
electrode together create a second inactivation zone within the
interior of the ducting section.
7. An air treatment apparatus for removal of health threatening
airborne pollutants from an airflow, the air treatment apparatus
comprising: a ducting section defining an interior and a closed
end; an air inlet port for entry of airflow into the apparatus, the
air inlet being configured to facilitate establishing a generally
circular fluid motion; an exit port opposing the air inlet port; an
ultraviolet light source disposed within the interior of the
ducting section, the ultraviolet light source creating an
inactivation zone within the ducting section, wherein the air flow
and airborne pollutants are urged into the inactivation zone as the
airflow travels in an inward generally circular direction downward
through the ducting section toward the exit port to ensure multiple
exposures of airborne pollutant material into the inactivation zone
whereby purified air exits through the exit port.
8. The air treatment apparatus as claimed in claim 7, wherein the
ducting section has a generally cylindrical shape.
9. The air treatment apparatus as claimed in claim 7, wherein the
ducting section includes an ultraviolet reflective layer coated on
an interior surface of the cylindrical ducting section.
10. The air treatment apparatus as claimed in claim 9 wherein
ultraviolet light source is positioned opposing the ultraviolet
reflective layer within the interior of the cylindrical ducting
section.
11. The air treatment apparatus as claimed in claim 9, wherein the
ultraviolet light source emits ultraviolet rays reflecting off the
reflective layer creating the inactivation zone.
12. An air treatment apparatus for removal of health threatening
airborne pollutants from an airflow, the air treatment apparatus
comprising: a ducting section comprising a first section and a
second section having a closed end; an air inlet port for entry of
airflow into the first ducting section, the air inlet being
configured to establish a generally circular fluid motion of the
airflow within an interior of the ducting section; an exit port in
the first ducting section; a plasma-generating flexible electrode
disposed about an inner wall surface of the first ducting section;
an ultraviolet light source disposed within the interior of the
second ducting section; wherein the plasma-generating flexible
electrode and the ultraviolet light source together create an
inactivation zone within the ducting section, wherein the airflow
and airborne pollutants are urged into the inactivation zone as the
airflow travels in an inward generally circular direction through
the first ducting section toward the closed end of the second
ducting section thereby increasing a pressure of the air flow in
the closed end of the ducting section and urging the airflow in an
opposing outward direction toward the exit port to ensure multiple
exposures of airborne pollutant material into the inactivation zone
as the airflow travels in the inward direction and in the opposing
outward direction whereby purified air exits through the exit
port.
13. The air treatment apparatus as claimed in claim 12 wherein the
first ducting section has a cylindrical shape and the second
ducting section comprises a conical shape.
14. The air treatment apparatus as claimed in claim 12 wherein the
inward airflow is generally in a spiralling pattern with continuous
rotating flow in a plurality of planes as it travels in a first
direction from the inlet through the apparatus to the closed end of
the apparatus, and wherein the outward airflow is generally in one
plane, which is along a longitudinal axis of the apparatus thereby
increasing the exposure of airborne pollutants in the airflow to
the inactivation zone.
15. An air treatment apparatus for removal of health threatening
airborne pollutants from an airflow, the air treatment apparatus
comprising: a ducting section defining an interior; an air inlet
port in a top of the ducting section for entry of airflow into the
apparatus; an exit port in a bottom of the ducting section and
opposing the air inlet port; a device disposed within the interior
for creating an inactivation zone within the interior of the
ducting section, wherein the airflow and airborne pollutants are
urged into the inactivation zone as the airflow travels in an
inward circular direction through the ducting section toward the
bottom of the ducting section and the exit port to ensure multiple
exposures of airborne pollutant material into the inactivation zone
as purified air exits through the exit port.
16. The air treatment apparatus as claimed in claim 15, wherein the
ducting section has a longitudinal cylindrical shape.
17. The air treatment apparatus as claimed in claim 15, wherein the
device is a plasma-generating flexible electrode.
18. The air treatment apparatus as claimed in claim 15, wherein the
device is an ultraviolet source.
19. The air treatment apparatus as claimed in claim 15, wherein the
device is a combination plasma-generating flexible electrode and an
ultraviolet light source.
20. The air treatment apparatus as claimed in claim 15, wherein the
inactivation zone is a length of the interior of the ducting
section from the top to bottom.
Description
TECHNICAL FIELD
[0001] The present invention relates to an air treatment method and
apparatus. More specifically, the invention relates to an air
treatment apparatus which may comprise a flexible electrode
assembly and an air ducting system. The apparatus may further
comprise a power source. The electrode assembly is made of flexible
materials and used to generate low power electrical discharge
plasma for inactivating health threatening airborne pollutants
present in indoor air and removing pollutants from the same. The
present invention also provides a method of using such an apparatus
in air treatment applications for removal of health threatening
airborne pollutants.
[0002] In a further aspect, the present invention also provides an
air treatment apparatus for removal of health threatening airborne
pollutants, which may include pathogens, from an airflow, the air
treatment apparatus comprising an apparatus having a pre-determined
geometry the apparatus defining an area of generally circular fluid
motion, rotating in the same direction, the apparatus having an air
inlet for entry of airflow into the apparatus, and the air inlet
being configured to facilitate establishing the generally circular
fluid motion, and means being provided within the apparatus to
inactivate the health threatening airborne pollutants and an exit
from the apparatus from which purified outward air will exit.
Ideally, in a preferred embodiment, the apparatus having a defined
geometry comprising the above defined flexible electrode assembly,
with the flexible electrode assembly provided about the walls of
the apparatus such that the airflow is directed towards the walls
of the apparatus such that the health threatening airborne
pollutants are urged towards and into the inactivation zone created
by the plasma discharged from the outward facing conductive layer
of the flexible electrode assembly.
[0003] In another aspect, the present invention relates to an air
treatment device comprising a plasma generating flexible electrode
electrostatic precipitator assembly for air disinfection and
pollution control wherein the plasma generating flexible electrode
electrostatic precipitator assembly comprises the flexible
electrode assembly configured for generating low power electrical
discharge plasma and for inactivating pathogens in the airflow. In
yet a further embodiment, the inactivation zone can be created from
use of an ultraviolet light source alone or in combination with the
plasma generating flexible electrode.
BACKGROUND
[0004] Health threatening airborne pollutants may be subdivided
into three groups; (a) airborne pathogens comprising any organism
that causes disease that spreads throughout the environment via the
air; (b) airborne allergens comprising any substance that, when
ingested, inhaled, or touched, causes an allergic reaction and, (c)
airborne volatile organic compounds (VOC) comprising any product
that is designed to be sprayed at high pressure in the form of tiny
particles that remain suspended in the air. The last category
includes many cleaning chemicals, hair spray, various types of
primer, and fuels such as gasoline and kerosene, as well as other
household, beauty, or hobby products. Some fabrics, particularly
those recently manufactured, also contribute to indoor airborne
VOCs when they outgas, or leak out chemicals in gaseous form, over
time.
[0005] Airborne pollutants can build up significantly in indoor
environments with the result that the air that we breathe may
become contaminated. Considering that on average humans spend
approximately 90% of their time in an indoor environment, it will
be appreciated that the removal of pollutants from indoor air is of
importance to reduce allergies and prevent infection transmission,
such as sick building syndrome.
[0006] Existing state of the art technologies for the control of
airborne pathogens can be categorized as: (a) airborne trapping
systems or filters, (b) airborne inactivation systems and, (c) some
combination of the above.
[0007] Existing airborne inactivation technologies also include
those that make use of chemicals, UV radiation and plasma discharge
by-products.
[0008] Examples of chemical inactivation include the use of
antimicrobial vaporizers, typically ozone or hydrogen peroxide.
While these systems are effective, they are also disruptive,
requiring the evacuation of indoor space to be treated and
therefore are not suitable for use under normal living
circumstances.
[0009] Alternative inventions for the purification of air comprise
the use of ultra violet light (UV) emission to kill airborne
bacteria. For example, international publication No. WO
2003/092751, describes a device in which a fluid (e.g. air) is
passed through an array of UV lamps. It is appreciated that in this
solution the one and only inactivation mechanism is via UV
radiation.
[0010] It is also known to use of plasma radicals for sterilisation
of air filter medium; see for example US patent publication No.
2004/0184972 A1. In this prior art document, it is proposed that an
upstream plasma discharge can generate active radicals which flow
upstream to a medium filter and kill any bacteria or virus trapped
by the filter.
[0011] In such systems which rely on plasma discharge, the design
and configuration of the plasma generator are of particular
importance. The teachings disclosed in the present document offers
an electrode assembly for plasma generation which can be used for
air disinfection and pollution control.
SUMMARY OF THE INVENTION
[0012] Accordingly, a first embodiment of the application provides
a flexible electrode assembly for an air treatment device as
detailed in claim 1. Accordingly, in one aspect, the present
invention provides a flexible electrode assembly for an air
treatment device comprising: [0013] a flexible dielectric layer
forming an insulating sheet; [0014] a plurality of conductive
tracks on a first side of the insulating sheet; [0015] a uniform
electrically conducting material with no gaps or holes forming a
conductive layer on a second side of the insulating sheet; and
[0016] an AC power source having a voltage source frequency
equivalent to mains frequency and configured to provide power to
the electrode assembly such that ionization generated by the
assembly is a dark or Townsend type discharge, the power source
being further configured to operably ensure that power per unit
area applied to the electrode assembly is less than 100
mW/cm.sup.2; [0017] and wherein supply of voltage to the conducting
tracks and the conductive layer generates plasma which is
discharged from the conducting tracks and further wherein the
plurality of conductive tracks form a first layer of the assembly
and the conductive layer forms a second layer of the assembly, the
supply of voltage to the first layer and the second layer generates
a dielectric barrier discharge type plasma which is discharged and
sustained only from the first layer.
[0018] An advantage of the flexible electrode of the present
invention is that it can take the form of any desired shape and can
conform to the shape of an apparatus into which it is inserted such
as the inside of a duct or a ducting section including an apparatus
having a generally conical geometry comprising a cylindrical
section and a conical section.
[0019] In another aspect, the present invention also provides an
air treatment system and air treatment apparatus as detailed in the
independent claim(s). Advantageous embodiments are provided in the
dependent claims.
[0020] In a further aspect, the present invention also provides an
air treatment apparatus for removal of health threatening airborne
pollutants, which may include pathogens, from an airflow, the air
treatment apparatus comprising an apparatus having a pre-defined
geometry; the apparatus defining an area of generally circular
fluid motion, rotating in the same direction, the apparatus having
an air inlet for entry of airflow into the apparatus, and the air
inlet being configured to facilitate establishing the generally
circular fluid motion, and means being provided within the
apparatus to inactivate the health threatening airborne pollutants
and an exit from the apparatus from which purified outward air can
exit. Ideally, in a preferred embodiment, the exit from the
apparatus is coplanar with the plane of the direction of the
swirling airflow in the apparatus; but the outward airflow
direction is opposite from the inward swirling airflow direction.
Other features are included in the dependent claims.
[0021] An advantage of the air treatment apparatus of the invention
is that the spiralling airflow ensures that the pathway of any
airborne pollutant material through the apparatus is relatively
long so that the time spent in the apparatus is also longer than
would be the case with a direct inward airflow longitudinally
through the apparatus; hence the number of times that an airborne
pollutant material will be urged into the inactivation zone is
increased relative to a linear inward airflow. A further advantage
is that the outward airflow out of the apparatus then removes the
inactivated airborne pollutant material so that no build-up of
material occurs inside the cyclone geometry apparatus.
[0022] In one preferred embodiment, the present invention relates
to an air treatment device comprising a plasma generating flexible
electrode and electrostatic precipitator assembly for air
disinfection and pollution control wherein the plasma generating
flexible electrode electrostatic precipitator assembly comprises
the flexible electrode assembly configured for generating low power
electrical discharge plasma.
[0023] In one aspect, the present invention provides air treatment
apparatus comprising: [0024] an electrostatic precipitator
configured to charge airborne particles in the vicinity of the
electrostatic precipitator to provide charged airborne particles;
and [0025] a plasma generator comprising the flexible electrode
assembly, positioned in proximity to but at a pre-determined
distance from the electrostatic precipitator and configured for
cooperation with the electrostatic precipitator, the plasma
generator configured to create an inactivation zone in the region
of the plasma generator; and wherein the air treatment device
comprises means for directing the charged airborne particles
generated by the electrostatic percipitator into the inactivation
zone such that the air treatment device is adapted to generate
charged airborne particles and then immediately, to direct the
charged airborne particles into the inactivation zone so as to
expose the charged airborne particles to plasma in the inactivation
zone. The means for directing the charged airborne particles
generated by the electrostatic percipitator into the inactivation
zone may comprise a voltage applied between the electrostatic
precipitator and the plasma generator such that the air treatment
device is adapted to generate charged airborne particles and, at
the same time, to direct the generated charged particles, by
attracting said charged airborne particles towards the plasma
generator, into the inactivation zone so as to expose the charged
airborne particles to plasma in the inactivation zone.
[0026] It is to be understood that throughout this patent
specification, the term, "inactivation zone" refers to a zone in
which plasma is released and is effective to inactivate airborne
pollutant material including pathogens. Such airborne pollutant
material (i.e. airborne pollutants), which can be health
threatening, may be subdivided into three groups: (a) airborne
pathogens comprising any organism that causes disease that spreads
throughout the environment via the air; (b) airborne allergens
comprising any substance that, when ingested, inhaled, or touched,
causes an allergic reaction and, (c) airborne volatile organic
compounds (VOC) comprising any product that is designed to be
sprayed at high pressure in the form of tiny particles that remain
suspended in the air. The plasma generated by the plasma generator
in the air treatment apparatus of the present invention is
effective to inactivate any of the airborne pollutant materials as
defined in subdivisions (a) to (c).
[0027] Thus, the air treatment apparatus is configured to attract
the charged airborne particles into the inactivation zone; this is
not the same as trying to attract all the charged particles onto
the surface of the plasma generator as in fact, such would be
undesirable as it could interfere with the effective operation of
the plasma generator if all the charged particles were on the
surface of the plasma generator.
[0028] The air treatment apparatus of the present invention
comprises a plasma generator, preferably a flexible electrode
assembly for generating plasma, which is configured to operate at a
power density less than 1 W/cm.sup.2 to operably generate a plasma
discharge.
[0029] In the preferred embodiment, the plasma generator comprises
a flexible electrode assembly, flexible electrode assembly which is
configured to operate at a power density less than 1 W/cm.sup.2 to
operably generate a plasma discharge circumferentially about a
longitudinal axis of the flexible electrode assembly. It is to be
understood that although the flexible electrode assembly may be
provided on at least a portion of the inside walls of the air
treatment apparatus, preferably, circumferentially about at least a
portion of the inside walls, but that the flexible electrode
assembly can be of any desired dimensions that is sufficient to
provide an inactivation zone in the region of the walls of the
apparatus. The inactivation zone extends outwardly from the
flexible electrode assembly by up to approx. 1 cm. It is not
necessary for the airborne pollutant material to collide with the
flexible electrode assembly in order for the airborne pollutant
material to be inactivated; it is sufficient for the airborne
pollutant material to enter into the inactivation zone. Ideally, in
the air treatment apparatus of the present invention, airborne
pollutant material will enter into the inactivation zone multiple
times due to the rotating, swirling motion of the inward airflow.
This inward airflow is directed into the air treatment device
through an inward airflow port which is configured to establish
cyclonic airflow. The airflow port comprises a plurality of walls
which cooperate to establish cyclonic airflow.
[0030] Most preferably, the plasma generator is configured to be
operated at a power density in the range from 0.1 to 0.5 W/
cm.sup.2. This is a relatively low power density for plasma
generation and is effective for creating an inactivation zone about
the plasma generator.
BRIEF DESCRIPTION OF THE DRAWINGS
[0031] The present application will now be described with reference
to the accompanying drawings in which are shown, by way of example
only, a number of aspects and embodiments of the present
invention:
[0032] FIG. 1 is a view from a first side of an electrode assembly
in accordance with the present teachings;
[0033] FIG. 2 is a view of the electrode assembly of FIG. 1 from a
second side;
[0034] FIG. 3 is a view from the first side of the electrode
assembly bent in a semi-circular manner in accordance with the
present teachings;
[0035] FIG. 4 is a view from the second side of the electrode
assembly bent in a semi-circular manner in accordance with the
present teachings;
[0036] FIG. 5 is a view of the flexible electrode assembly in
accordance with the present teachings deployed within a
conduit;
[0037] FIG. 6 is a close up view of the flexible electrode assembly
of FIG. 5 deployed within the conduit;
[0038] FIG. 7 is a view of an alternative configuration for the
deployment of the flexible electrode assembly within a conduit;
and
[0039] FIG. 8 is a cross section view of the alternative deployment
configuration of FIG. 7;
[0040] FIG. 9 is a schematic diagram showing the connection for
power supply to the first layer of the flexible electrode flexible
electrode assembly, that is the plasma-generating surface of the
flexible electrode; and the second layer of the flexible electrode
assembly, that is the rear side of the flexible electrode;
[0041] FIG. 10 is a perspective view of one embodiment of an air
treatment apparatus which is in a form of a generally cyclonic
geometry comprising a generally cylindrical section and a generally
conical section;
[0042] FIG. 11 is a cross sectional view of the air treatment
apparatus of FIG. 10 showing the spiralling downwardly inward
airflow and the upwardly directed outward airflow;
[0043] FIG. 12 is a cross sectional view from above, showing the
angular airflow inlet arranged tangentially to the direction of the
airflow within the cyclonic geometry air treatment apparatus;
[0044] FIG. 13 is a cross sectional view of another embodiment of
the air treatment apparatus showing the flexible electrode assembly
of FIGS. 1 to 4 shown arranged about the inside walls of the
cylindrical section of the cyclonic geometry;
[0045] FIG. 14 is a cross sectional view of another embodiment of
the air treatment apparatus; which comprises the same features as
the embodiment of
[0046] FIG. 13 except that the apparatus is inverted i.e. turned
through an angle of 180 degrees relative to the apparatus as shown
in FIG. 13; this demonstrates that the apparatus does not operate
in the same manner as a conventional cyclone which is typically
used for separation of components and the present invention is
entirely different from that function;
[0047] FIG. 15 is a side sectional view of another embodiment,
similar to that shown in FIG. 13 with the flexible electrode
assembly included;
[0048] FIG. 16 is a further view of the embodiment shown in FIG.
14;
[0049] FIG. 17 is a side sectional view of another embodiment,
similar to that shown in FIGS. 13 and 15, with the flexible
electrode assembly included in the cylindrical section of the air
treatment assembly and the flexible electrode extending longer
distance along the length of the cylindrical section of the air
treatment apparatus;
[0050] FIG. 18 is a further view of the embodiment shown in FIG.
17;
[0051] FIG. 19 is an alternative perspective view of the air
treatment apparatus of FIG. 13;
[0052] FIG. 20 is an alternative embodiment of the air treatment
device shown in FIG. 11 incorporating an alternative means of
inactivating the health threatening pollutant materials in the
airflow is employed, for instance using a UV light source,
optionally located at or in the region of the closed end of the
device; and with the airflow being indicated by the arrows shown in
FIG. 20; in this embodiment, the inner walls of the air treatment
device are coated with a UV reflective layer such that the UV light
rays from the UV light source reflect internally in the manner
shown by the arrows in FIG. 21;
[0053] FIG. 21 is a further view of the embodiment of the air
treatment device shown in FIG. 20 using UV light source provided
within the device, optionally, at or in the region of the closed
end of the device and having the inner walls of the air treatment
device coated with a UV reflective layer such that the UV light
rays from the UV light source reflect internally in the manner
shown by the arrows;
[0054] FIG. 22 is a further alternative embodiment of an air
treatment apparatus in which an electrostatic precipitator is
included in the air treatment apparatus for cooperation with the
flexible electrode assembly; the electrostatic precipitator, in
this embodiment shown in FIGS. 22 and 23, is in the form of a
needle array; and
[0055] FIG. 23 is an exploded view of the air treatment apparatus
of FIG. 22 showing the needle electrode electrostatic precipitator
in more detail;
[0056] FIG. 24 is a further alternative embodiment of an air
treatment apparatus in which a UV light source is incorporated into
the air treatment apparatus for cooperation with the flexible
electrode assembly
[0057] FIG. 25 shows a cyclone duct pathway that is also adapted to
provide the airflow pattern indicated by the arrows;
[0058] FIG. 26 is a graphical representation showing the air speed
inside the cyclone equivalent duct path with the air speeds in the
sections A, B and C shown in FIGS. 25;
[0059] FIG. 27 is an alternative embodiment in which the air
treatment apparatus has a cylindrical profile with arrows showing
the airflow pathway through the cylindrical configuration;
[0060] FIG. 28 is a cross sectional view showing the airflow
pathway through the apparatus of FIG. 27 using the UV light
source;
[0061] FIG. 29 is a cross sectional view with the arrows showing
the UV rays in the air treatment apparatus using the UV light
source located in the device;
[0062] FIG. 30 is a partial cutaway perspective view showing the
inner electrode and the outer electrode arrangement in the
embodiment of FIGS. 29 and 30 in which the apparatus has a
cylindrical profile; and,
[0063] FIGS. 31a and 31b is an alternative embodiment in which the
apparatus has a cylindrical profile, incorporating both the
flexible electrode assembly in cooperation with the UV light
source.
DETAILED DESCRIPTION
[0064] The present teachings relate to an air treatment apparatus
or device comprising a flexible electrode assembly which is used
with a ducting system to operably generate a plasma for treatment
of air passing through the ducting system. The apparatus may
further comprise a power source which is coupled to the flexible
electrode assembly to provide power which is used in the generation
of a plasma. In addition, an impeller may be required to force air
through the ducting system. By providing such a combination of
elements, it is possible, when power is applied to the electrode
assembly, to generate a low power plasma discharge field to
effectively sterilise air of micro-organisms or pathogens or
oxidise organic airborne contaminants and particles that are
passing through the ducting system.
[0065] In an alternative embodiment, the present disclosure relates
to an air treatment apparatus or device comprising a ultraviolet
(UV) light source which is used with a ducting system for treatment
of air passing through the ducting system. In yet a further
alternative embodiment, the present disclosure relates to an air
treatment apparatus or device comprising a flexible electrode
assembly in combination with a UV light source used with a ducting
system to operably generate a plasma and UV rays for treatment of
air passing through the ducting system.
[0066] The power source may be a high voltage generator with
voltage output in the range 1 kV to 10 kV amplitude. The high
voltage generator may be of continuous (DC) or alternating (AC)
current type. An exemplary embodiment is driven by an AC power
source. In this embodiment the voltage source frequency is the same
as mains frequency, i.e. 50 to 60 Hz depending on the geographical
region. In an alternative embodiment the frequency of the power
supply may be in the kilo-Hertz range; e.g. 1 kHz to 250 kHz.
Further alternative embodiments may be fitted with AC power
supplies with modulation frequency in the range above or below
those listed above. The configuration of the flexible electrode
assembly is best described with reference to FIGS. 1 and 2, which
show an electrode assembly 100 comprising a dielectric layer 101 to
which electrodes are attached on front and back sides of the
dielectric layer 101. In this way, the electrodes are provided on
opposing sides of the dielectric layer. The electrodes each
comprise a conductive layer. A first conductive layer 102 is
patterned as a series of thin rows of electrically conducting
tracks leaving a narrow gap between the rows. The second conductive
layer 203 (shown in FIG. 2) comprises a uniform electrically
conducting material with no gaps or holes therein. The first 102
and second 203 conductive layers act as a pair of electrodes.
[0067] A plasma discharge is generated by applying power to the
pair of electrodes comprising the first conductive layer 102 and
the second conductive layer 203. The applied power sustains either
a DC or an AC discharge from the first surface 102 of the flexible
electrode assembly 100. The plasma generation in the present
teachings is of a dielectric barrier discharge (DBD) type with both
electrodes insulated from one another by the dielectric layer 101.
The configuration and positioning of the first 102 and second 203
conductive layers ensures that the plasma discharge is generated
and sustained on the first layer 102 of the electrode assembly
100.
[0068] Dielectric-barrier discharge (DBD) is an electrical
discharge between two electrodes i.e., the first layer 102 and the
second layer 203 separated by an insulating dielectric barrier
i.e., the dielectric sheet 101. Known DBD devices are typically
planar, using rigid parallel plates separated by a dielectric or
cylindrical, using coaxial plates with a dielectric tube between
them. However, by using flexible materials for the construction of
the electrode assembly 100 in accordance with the present
teachings, one can assemble an electrode pair with flexible
characteristics, thereby allowing the device to be shaped to
geometries other than planar or cylindrical arrangements.
[0069] The dielectric layer 101 is made of a suitable insulating
material with a high dielectric strength, which can be chosen as
appropriate by those skilled in the art. In an exemplary
arrangement of the present teachings, the dielectric insulating
layer 101 comprises a polyimide insulating sheet with dielectric
strength greater than 100 kV/mm.
[0070] In this exemplary arrangement, the electrode assembly 100
consists of a polyimide sheet with a copper sheet on one side
(acting as the second conductive layer 203) and copper tracks on
the opposite side (acting as the first conductive layer 102).
[0071] The use of polyimide with copper attached thereto is well
known for manufacturing printed circuit boards. In particular such
configuration may generally constitute a flexible printed circuit
board. It is appreciated that such flexible circuits are
assembled/manufactured in a planar form and become a bendable or
flexible sheet/board arising out of the physical characteristics of
the materials used. It is also noted that these bendable boards are
typically designed to allow flexibility where traditional rigid
printed circuit boards are not suitable; e.g. when conforming to
non-planar enclosures or surfaces is required. As such these
flexible printed circuit boards are used in similar applications as
their rigid counterparts including low voltage and low current
usage but heretofore have not been used in the context of a plasma
generator.
[0072] The inventors of the present application have appreciated
that these flexible boards can be configured for use as an
electrode assembly or electrode assemblies for generating medium to
high power plasma discharges; i.e. discharges where power per unit
area is in excess of 1 W/cm.sup.2. However, under such operating
conditions, the lifetime of such flexible printed circuit boards
tends to be reduced due to the high voltage and power applied which
may cause short circuiting on the board and burn out the tracks due
to high current. Therefore, it is important that the power provided
to the flexible printed circuit boards in accordance with the
present invention is carefully regulated.
[0073] According to the teachings of the present invention, the
power applied to the electrode assembly 100 by the power source is
to be low enough to limit the amount of ionization of the air in
the vicinity of the electrode assembly 100 and to keep low
electrical stress on the PCB to ensure long operating lifetimes. In
an exemplary aspect, the power per unit area applied to the
electrode is below 100 mW/cm.sup.2. At this power level, the
ionization generated by the system is of the type of a dark or
Townsend discharge. As is known to those skilled in the art, this
discharge mode is characterized by a combination of low discharge
currents (in the range of micro amperes or lower) and no radiative
emission, hence the term dark. The generation of radicals in this
discharge mode is also limited, which is advantageous in order to
maintain a low level of anti-pathogenic agents released by the
system of the present invention. The ionized plasma is therefore
not of a glow discharge mode where the plasma current and radical
and other plasma species concentration is significantly higher
resulting in a visible glow, electrode heating and damage and
significant release of toxic radicals.
[0074] In another aspect, the electrode assembly 100 may include an
additional insulating layer between the first conducting layer 102
and the dielectric layer 101. Additionally or alternatively, an
insulating layer may be placed between the second conductive layer
202 and the dielectric layer 101. Such an additional layer(s)
serves to protect the dielectric layer 101 from external sources of
contamination or degradation. The additional protective layer(s)
also reduces the possibility of arcing between the layers acting as
electrodes and/or nearby conductors.
[0075] FIGS. 3 and 4 show perspective views of the electrode
assembly 100 when bent in a semi-circular manner with the first
conductive layer 102 on the inner side and the second conductive
layer 203 on the outer side. Specifically, FIG. 3 shows the inner
side of the electrode assembly 100 when bent to be arcuate while
FIG. 4 shows the outer side of the electrode assembly 100.
[0076] Although a semi-circular shape is shown, a plurality of
shapes can be formed using the flexible electrode assembly 100. In
a preferred embodiment, the shaped formed using the flexible
electrode assembly 100 comprises a conical geometry.
[0077] It will be understood by those skilled in the art that power
is provided from a power supply to the flexible electrode assembly
100. The exact nature of the connection (e.g., wiring) between the
flexible electrode assembly 100 and the power supply can be chosen
as appropriate and it is not necessary that the power supply and
the electrode assembly 100 be co-located. A transformer (not shown)
may also be used between the power supply and the flexible
electrode assembly 100 to provide high-voltage alternating
current.
[0078] The first 102 and second 203 conductive layers maintain
direct contact around their respective total surface areas with the
dielectric layer 101. This ensures that there are no air pockets
within the electrode assembly 100 where elevated levels of plasma
can build up during generation of plasma.
[0079] In the preferred aspect of the present teachings, the
continuous uniform material of second conductive layer 203 ensures
no plasma is sustained on the second layer 203 of assembly 100. On
the other hand, the rows of wire separated by gaps in the first
conductive layer 102 allows high electric fields to build up in the
gaps due to the high voltage potential applied between the first
conductive layer 102 and second 203 conductive layers. This
electric field ionizes the gas in the vicinity of the first
conductive layer 102 initiating and sustaining an atmospheric
plasma discharge. Said plasma discharge is limited to the first
surface 102. Furthermore, said plasma discharge generates an
inactivation zone above the first conductive layer 102 of the
electrode assembly 100 where the plasma field, radiation and active
species act as anti-pathogenic agents for the air passing the
flexible electrode assembly 100.
[0080] An inactivation zone is a zone in which plasma is released
and is effective to inactivate airborne pollutant material
entrained in the airflow. Health threatening airborne pollutants
may be subdivided into three groups: (a) airborne pathogens
comprising any organism that causes disease that spreads throughout
the environment via the air; (b) airborne allergens comprising any
substance that, when ingested, inhaled, or touched, causes an
allergic reaction and, (c) airborne volatile organic compounds
(VOC) comprising any product that is designed to be sprayed at high
pressure in the form of tiny particles that remain suspended in the
air.
[0081] It will be understood by those skilled in the art that
replacing the second conductive layer 203 (i.e., a sheet of
conductive material) with a layer similar to that of the first
conductive layer 102 (having rows of wire separated by gaps) will
result in a plasma discharge being generated and sustained on the
second side of the flexible electrode assembly 100 as well as on
the front side. This may be desirable under some circumstances
and/or applications of the present teachings and it is not intended
to limit the present teaching to generation of a plasma on one side
only of the electrode assembly.
[0082] The flexible electrode assembly 100 should preferably be
oriented in a manner that airflows in parallel direction to the
direction of the assembly so as to maximise the time that the air
is exposed to the plasma that is generated by the assembly. By
providing a flexible assembly the inactivation zone that is
generated by the electrode assembly does not need to be planar as
the assembly may adopt various curved geometries. In particular,
due to the flexible nature of the electrode assembly 100 of the
present teachings, a plurality of configurations are possible.
[0083] FIG. 5 illustrates one such exemplary configuration. It can
be seen that a plurality of the flexible electrode assemblies 100
are deployed within a circular conduit 504. The conduit 504 is
shown with a cut away for ease of viewing of the plurality of
flexible electrode assemblies 100 within the conduit. As will be
understood by those skilled in the art any suitable shaped conduit
may be used and the flexible nature of the assembly allows it adopt
the shape of the conduit 504. Air enters the conduit 504 in the
direction of arrow 505, flows past a plurality of electrode
assemblies 100 and exits at the other end of the conduit 504.
[0084] FIG. 6 is a close up image of the flexible electrode
assembly of FIG. 5. It can be appreciated that a plurality of
electrode assemblies 100 are shaped to match or adopt the interior
curvature of the conduit 104. Furthermore, the individual electrode
assemblies 100 can be positioned relative to one another to form a
continuous ring of electrode assemblies within the conduit. It
should be understood that in some configurations, fewer electrode
assemblies 100 may be used. For example, although four assemblies
100 are shown in FIGS. 5 and 6, two or three assemblies 100 could
be used in non-contiguous ring. The determination of the number of
assemblies may be chosen as appropriate by the skilled person. In
some circumstances, a single assembly may be used provided that the
inactivation zone created by the plasma discharged from the first
layer of the flexible electrode assembly 100 is sufficient to
inactivate airborne pollutant material entrained in the airflow
505.
[0085] A number of means known to those skilled in the art could be
chosen to induce airflow through the conduit 504, for example, an
impeller may be used.
[0086] The plasma concentration in the inactivation zone, created
by the plasma discharged from the first layer 102 of the flexible
electrode assembly 100, is be sufficient to effectively inactivate
airborne pollutant material entrained in the airflow. Furthermore,
the concentration of plasma should decay sufficiently outside the
inactivating zone so that the concentration of any anti-pathogenic
agents created by the plasma discharge in the cleaned air expelled
from the conduit 504 regions of the apparatus is at a
physiologically acceptable level.
[0087] FIG. 7 illustrates another configuration for the deployment
of at least one flexible electrode assembly 100 within a conduit
706. A cut out section of the conduit 706 is provided in FIG. 7 to
for ease of visualization. A plurality of electrode assemblies 100
are provided within a restricted rectangular section 708 of conduit
706. Specifically, the plurality of electrode assemblies 100 are
positioned on the interior surface of the rectangular section 708
to form a continuous ring of electrode assemblies. It will be
appreciated that the flexible nature of the electrode assemblies
ensures that easily configured to form a continuous ring within the
rectangular section 708.
[0088] Air enters the conduit 706 in the direction of arrow 707,
flows into a rectangular section 708 of the conduit 706 fitted with
a plurality of flexible electrode assemblies 100. The shape of said
section 708 is such that air flowing past the electrode assemblies
100 shall do so within one centimetre from the first conductive
layer 102 of the electrode assemblies present in the section 708.
This means that the electrode assemblies at the top and bottom
interior surfaces of the rectangular section 708 cannot be more
than one centimetre apart. However, the distance between the sides
can be much more than one centimetre.
[0089] The arrangement of FIG. 7 ensures that any volume of air
flowing through the conduit 706 does so within the inactivation
zone resulting from the atmospheric plasma discharge. A cross
section of the configuration of FIG. 7 is shown in FIG. 8.
[0090] Referring now to FIG. 9 which shows the connection for power
supply to the first layer of the flexible electrode flexible
electrode assembly, i.e. the plasma-generating surface of the
flexible electrode assembly; and the second layer of the flexible
electrode assembly, i.e. the rear side of the flexible electrode
assembly, that is the side of the flexible electrode assembly that
is adjacent to the wall of the ducting section or air treatment
apparatus. Plasma is generated by the flexible electrode assembly
100 by applying power to the pair of electrodes, that is, the first
layer 102 and the second layer 203. The plasma is discharged from
only the first layer 102 so as to provide an inactivation zone in
the region of the first layer 102. The second layer 203 will
typically be abutting against the surface of a portion of an inside
wall of a ducting section or air treatment apparatus as will be
shown in another aspect of the present invention which will be
further described with reference to other Figures herein. The
applied power sustains either a DC or an AC discharge between,
around and/or on the surface of the electrode pair comprised of the
first layer 102 and the second layer 203 of the flexible electrode
assembly. It is to be understood that the arrangement shown in FIG.
9 is only one embodiment of the arrangement for the flexible
electrode assembly 100 which, by way of example, is shown as being
an AC voltage supply to the first layer 102 and the second layer
203. As also shown in FIG. 9, in this particular embodiment, a DC
voltage such as in the range of between 1,000 V and 10,000 V (1 kV
to 10 kV); preferably in the range of between 2,000 and 9,000
volts; more preferably in the range of between 3,000 and 8,000
volts; most preferably in the range of between 4,000 and 7,000
volts; and ideally, is at a voltage of about 5,000 volts, is
applied between the electrostatic precipitator such as the needle
electrode array such as in the arrangement shown in FIGS. 20 and
21; and the outer layer 102 of the flexible electrode assembly
plasma generator 100.
[0091] It will be appreciated that the voltage and current
parameters required to achieve a dielectric barrier discharge will
depend principally on the nature of the dielectric used. In
general, operating voltages below 1 kV are not practical, and
preferably, an operating voltage in the range from 1 to 6 kV is
provided between the first layer and the second layer of the
flexible electrode assembly, most desirably, a voltage of from 3 to
5 kV is provided between the first layer and the second layer of
the flexible electrode assembly, for example about 4 kV. It will be
appreciated that the current required to maintain the dielectric
barrier discharge is significantly less than that required to
initiate it. The current (and hence the power) of plasma generator
units is normally expressed in terms of the starting current. There
should be used a (starting) current in the range from 1 to 10 mA,
preferably at least 3 mA. The power of the plasma generator will,
of course, depend on the voltage and current combination. The power
should generally be not more than 50 watts, and is preferably at
least 4 watts. Typically, the power is in the range from 10 to 40
watts. These power levels have in particular been found to be
convenient where the plasma generator is used as part of an
apparatus unit having a conduit volume of the order of 0.02 to 1.0
m3.
[0092] Referring now to FIGS. 10 to 16, a number of embodiments of
an air treatment apparatus in accordance with the invention, will
be described.
[0093] The embodiment shown in FIGS. 10, 11 and 12 comprises an
impeller 1102 and an air inlet 1108 and the apparatus includes a
first section which is generally cylindrical and comprises an
airflow inlet; preferably wherein the flexible electrode assembly
(not shown in FIGS. 10-12) which is configured adjacent or in
abutment with the cylindrical section. The inward airflow as
indicated by arrows 1103 enters into the impeller 1102 and through
the air inlet port 1120 which has inner walls, including an arcuate
wall 1204, configured to established in a spiral, continuously
rotating airflow as it travels from the impeller housing 1302 and
into the apparatus inlet 1320 which is configured to establish a
spiralling airflow which is indicated by the arrows 1206 in the
cylindrical section of the apparatus and in the conical section
also. Then as the pressure in the closed end 1208 of the conical
section increases, the airflow direction is urged back out of the
conical section in the direction of the arrow 1207 along the
longitudinal axis of the apparatus and out through the exit 1205 as
indicated by the arrows 1104. Thus the arrangement has particular
advantage as the spiralling pattern of the inward airflow as
indicated by the arrows 1106 ensures that airborne pollutant
material including pathogens in the airflow will be urged towards
the walls of the cylindrical section and the conical section at
least once, and more likely, several times during the travel in the
spiralling airflow 1206 due to the action of centrifugal forces.
Therefore, the airborne pollutant material will be urged into the
inactivation zone in the region of the plasma generating flexible
electrode assembly provided about the walls of the cyclone
geometry.
[0094] Referring to FIG. 13, the inward airflow 1303 is established
in a spiral, continuously rotating airflow as it travels from the
impeller housing 1302 and into the apparatus inlet 1320 which is
configured to establish the spiralling airflow 1306 in the
cylindrical section of the apparatus and in the conical section
also. Then as the pressure in the closed end 1308 of the conical
section increases, the airflow direction is urged back out of the
conical section in the direction of the arrow 1307 along the
longitudinal axis of the apparatus and out through the exit 1305 as
indicated by the arrows 1304. Thus the arrangement has particular
advantage as the spiralling pattern of the inward airflow as
indicated by the arrows 1306 ensures that airborne pollutant
material including pathogens in the airflow will be urged towards
the walls of the cylindrical section and the conical section at
least once, and more likely, several times during the travel in the
spiralling airflow due to the action of centrifugal forces.
Therefore, the airborne pollutant material will be urged into the
inactivation zone in the region of the plasma generating flexible
electrode assembly 1301 provided about the walls of the cyclone
geometry.
[0095] Thus the arrangement has particular advantage as spiralling
pattern of the inward airflow as indicated by the arrows 1306
ensures that airborne pollutant material including pathogens in the
airflow will be urged towards the walls of the cylindrical section
and the conical section at least once, and more likely, several
times during the travel in the spiralling airflow due to the action
of centrifugal forces. Therefore, the airborne pollutant material
will be urged into the inactivation zone in the region of the
plasma generating flexible electrode assembly 1301 provided about
the walls of the cyclone geometry. A further advantage of the air
treatment apparatus is that the spiralling airflow ensures that the
pathway of any airborne pollutant material through the apparatus is
relatively long so that the time spent in the apparatus is also
longer than would be the case with a direct inward airflow
longitudinally through the apparatus; hence the number of times
that an airborne pollutant material will be urged into the
inactivation zone is increased relative to a linear inward airflow.
A further advantage is that the outward airflow out of the
apparatus then removes the inactivated airborne pollutant material
so that no accumulation of material occurs inside the cyclone
geometry apparatus.
[0096] Referring now to the alternative embodiment shown in FIG.
14; which comprises the same features as the embodiment of FIG. 13
except that the apparatus is inverted i.e. turned through an angle
of 180 degrees relative to the apparatus as shown in FIG. 13; this
demonstrates that the apparatus does not operate in the same manner
as a conventional cyclone which is typically used for separation of
components and the present invention is entirely different from
that function. The air treatment apparatus shown in FIG. 14
operates in the same way as described for the embodiment of the air
treatment apparatus of FIG. 13. Like features are indicated with
like reference numerals to those used in FIG. 13. The cylindrical
section includes the flexible electrode assembly having the plasma
discharging first layer 1301. Again in this embodiment, the inward
airflow 1303' is established in a spiral, continuously rotating
airflow as it travels from the impeller housing 1302' and into the
apparatus inlet 1320' which is configured to establish the
spiralling airflow 1306' in the cylindrical section of the
apparatus and in the conical section also. Then as the pressure in
the closed end 1308' of the conical section increases, the airflow
direction is urged back out of the conical section in the direction
of the arrow 1307' along the longitudinal axis of the apparatus and
out through the exit 1305' as indicated by the arrows 1304'. Thus
the arrangement has particular advantage as the spiralling pattern
of the inward airflow as indicated by the arrows 1306' ensures that
airborne pollutant material including pathogens in the airflow will
be urged towards the walls of the cylindrical section and the
conical section at least once, and more likely, several times
during the travel in the spiralling airflow due to the action of
centrifugal forces. Therefore, the airborne pollutant material will
be urged into the inactivation zone in the region of the plasma
generating flexible electrode assembly 1301' provided about the
walls of the cyclone geometry.
[0097] Referring now to FIGS. 15 and 16, the air treatment
apparatus in this embodiment is substantially the same as that
shown in FIG. 13. Like features are referenced with like reference
numerals. The air treatment apparatus comprises a cyclone type
geometry comprising a cylindrical section and a conical section.
The cylindrical section includes the flexible electrode assembly
1401 having the plasma discharging first layer 1401a. There is an
impeller 1402 for directing inward airflow into the inward airflow
inlet indicated generally by reference numeral 1420 is established
in a spiral, continuously rotating airflow as it travels from the
impeller housing 1402 and into the apparatus inlet 1420 which is
configured to establish the spiralling airflow (not shown in FIGS.
15 and 16) in the cylindrical section of the apparatus and also in
the conical section. As the pressure in the closed end 1408 of the
conical section increases, the airflow direction is urged out of
the conical section along the longitudinal axis of the apparatus
and out through the exit 1405. Thus the arrangement has particular
advantage as the spiralling pattern of the inward airflow ensures
that airborne pollutant material including pathogens in the airflow
will be urged towards the walls of the cylindrical section and the
conical section at least once, and more likely, several times
during the travel in the spiralling airflow due to the action of
centrifugal forces. Therefore, the airborne pollutant material will
be urged into the inactivation zone in the region of the plasma
generating flexible electrode assembly 1401 provided
circumferentially about the walls of the cylindrical section of the
air treatment apparatus having the cyclone geometry.
[0098] It is to be understood that although the flexible electrode
assembly is shown in this embodiments in FIGS. 10 to 16 as
occupying only a portion of the walls of the cylindrical section of
the apparatus, that the flexible electrode assembly can be of any
desired dimensions that is sufficient to provide an inactivation
zone in the region of the walls of the apparatus. The inactivation
zone extends outwardly from the flexible electrode assembly by up
to approx. 1 cm. It is not necessary for the airborne pollutant
material to collide with the flexible electrode assembly in order
for the airborne pollutant material to be inactivated; it is
sufficient for the airborne pollutant material to enter into the
inactivation zone.
[0099] An advantage of the air treatment apparatus of the invention
is that the spiralling airflow ensures that the pathway of any
airborne pollutant material through the apparatus is relatively
long so that the time spent in the apparatus is also longer than
would be the case with a direct inward airflow longitudinally
through the apparatus; hence the number of times that an airborne
pollutant material will be urged into the inactivation zone is
increased relative to a linear inward airflow. A further advantage
is that the outward airflow out of the apparatus then removes the
inactivated airborne pollutant material so that no accumulation/
build-up of material occurs inside the cyclone geometry
apparatus.
[0100] Referring now to FIGS. 17 and 18, an alternative embodiment
of the air treatment device from that shown in FIGS. 10 to 16; is
exemplified. In the embodiment of FIGS. 17 and 18, the flexible
electrode assembly is shown as extending circumferentially about
the cylindrical section of the air treatment apparatus and
extending axially wider than in the embodiment shown in FIGS. 15
and 16. Thus in this embodiment, the flexible electrode assembly
occupies more of the region of the inner wall of the cylindrical
section of the air treatment apparatus than in the previous
embodiment in FIGS. 15 and 16. In FIGS. 17 and 18, like features
are again referenced with like reference numerals. The air
treatment apparatus comprises a cyclone type geometry comprising a
cylindrical section and a conical section. The cylindrical section
includes the flexible electrode assembly 1600 having the plasma
discharging first layer 1601. There is an impeller 1602 for
directing inward airflow into the inward airflow inlet indicated
generally by reference numeral 1620 is established in a spiral,
continuously rotating airflow as it travels from the impeller
housing 1602 and into the apparatus inlet 1420 which is configured
to establish the spiralling airflow (not shown in FIGS. 17 and 18)
in the cylindrical section of the apparatus and also in the conical
section. As the pressure in the closed end 1608 of the conical
section increases, the airflow direction is urged out of the
conical section along the longitudinal axis of the apparatus and
out through the exit 1605.
[0101] It is to be understood that the flexible electrode assembly
can be extended from the cylindrical section into the tapered
section of the cyclonic air treatment device. Indeed, the flexible
electrode assembly may, in an alternative embodiment, not shown in
the drawings, be provided in the conical section of the apparatus
rather than in the cylindrical section.
[0102] Indeed, the skilled person will understand that the
provision of the flexible electrode about the inner walls of the
cyclonic air treatment device can take several forms as the
function of the flexible electrode assembly is to generate plasma
for effective inactivation of airborne particles that are carried
in the airflow into the cyclonic air treatment device; the
preferred arrangement is to have the flexible electrode assembly
provided about at least a portion of the walls of the apparatus so
that the inactivation zone is created about the walls as that is
where the centrifugal forces will urge the inward airflow to travel
and hence airborne pollutant materials will be urged into the
inactivation zone. Hence the provision of the plasma-generating
flexible electrode assembly about at least a portion of the walls
enables cooperation between the action of the inward airflow
pattern and the inactivation zone to ensure multiple entries of
airborne pollutant material into the inactivation zone.
[0103] Referring to FIG. 19, the airflow inlet carrying air into
the cylindrical section is shown in more detail with reference to
the embodiment shown in FIG. 13. However, it is to be understood
that the airflow inlet shown in FIG. 19 is typical of the
construction of the airflow inlet in each of the embodiments shown
in FIGS. 10 to 18; and 20 to 24. The airflow inlet is configured to
generate a cyclonic type airflow and as such there is an arcuate
wall 1323 in cooperation with wall 1324, with the arcuate wall 1323
and 1224 being angled so as to initiate the cyclonic airflow that
is a swirling airflow with the inward airflow rotating repeatedly.
The airflow inlet also comprises walls 1321 and 1322 which function
to direction the inward airflow into the air treatment
apparatus.
[0104] Referring to FIGS. 20 and 21, an alternative embodiment of
the air treatment apparatus 1900 is shown in which an alternative
means for inactivating harmful pathogens and airborne particles is
included within the cyclonic air treatment apparatus 1900. In this
embodiment, the flexible electrode assembly is omitted and an
alternative means for inactivation such as a ultraviolet (UV) light
source 1950 is used in the closed end 1908 of the apparatus. The
air treatment apparatus 1900 comprises inner walls coated with a UV
reflective layer 1925 so that the UV light from the UV LED 1950 is
reflected throughout the air treatment device as indicated by the
arrows 1960 (Figure. 21).The air treatment apparatus 1900 also
comprises an impeller 1902, air inlet port 1924 and air outlet port
1905; thus the airflow direction in the air treatment apparatus
1900 is the same as that shown in FIG. 20 (indicated by the arrows
206 for the inward spiralling airflow and by the arrows 207 for the
outward linear flow). In this embodiment, the UV light emitted from
the UV light source 1950 shown in FIG. 21 in used to inactive
airborne pollution material.
[0105] Referring now to FIGS. 22 and 23, this further embodiment of
the air treatment apparatus 2000 of the present invention will be
described. In this embodiment, the air treatment apparatus 2000
comprises a plasma generating flexible electrode assembly 2101 for
generating plasma and creating an inactivation zone in a region of
about up to 1 cm outwardly from the flexible electrode assembly
layer. The apparatus 2000 also comprises an electrostatic
precipitator 2070 including a needle electrode array 2071 for air
disinfection and pollution control in conjunction with the cyclonic
arrangement wherein the plasma is generated from the first layer of
by the flexible electrode assembly 2101 configured for generating
low power electrical discharge plasma. As shown in FIG. 23, the
needle electrode array 2071 is provided before the inlet port to
the cylindrical section of the air treatment apparatus. FIG. 23 is
an exploded view of the air treatment apparatus 2000 of FIG. 22
showing the needle electrode electrostatic precipitator in more
detail.
[0106] In the embodiment shown in FIGS. 22 and 23, the air
treatment apparatus 2000 comprises an electrostatic precipitator
2070, 2071 configured to charge airborne particles in the vicinity
of the electrostatic precipitator to provide charged airborne
particles; and a plasma generator comprising the flexible electrode
assembly 2101 with a first layer for discharging plasma, positioned
in proximity to but at a pre-determined distance from the
electrostatic precipitator and configured for cooperation with the
electrostatic precipitator, the plasma generator configured to
create an inactivation zone in the region of the plasma generator;
and wherein the air treatment device comprises means for directing
the charged airborne particles generated by the electrostatic
percipitator into the inactivation zone such that the air treatment
device is adapted to generate charged airborne particles and then
immediately, to direct the charged airborne particles into the
inactivation zone so as to expose the charged airborne particles to
plasma in the inactivation zone. The means for directing the
charged airborne particles generated by the electrostatic
percipitator into the inactivation zone may comprise a voltage
applied between the electrostatic precipitator and the plasma
generator such that the air treatment device is adapted to generate
charged airborne particles and, at the same time, to direct the
generated charged particles, by attracting said charged airborne
particles towards the plasma generator, into the inactivation zone
so as to expose the charged airborne particles to plasma in the
inactivation zone.
[0107] The inactivation zone is a zone in which plasma is released
and is effective to inactivate airborne pollutant material
including pathogens. Such airborne pollutant material (i.e.
airborne pollutants), which can be health threatening, may be
subdivided into three groups: (a) airborne pathogens comprising any
organism that causes disease that spreads throughout the
environment via the air; (b) airborne allergens comprising any
substance that, when ingested, inhaled, or touched, causes an
allergic reaction and, (c) airborne volatile organic compounds
(VOC) comprising any product that is designed to be sprayed at high
pressure in the form of tiny particles that remain suspended in the
air. The plasma generated by the plasma generator in the air
treatment apparatus of the present invention is effective to
inactivate any of the airborne pollutant materials as defined in
subdivisions (a) to (c).
[0108] Thus, the air treatment apparatus 2000 is configured to
attract the charged airborne particles into the inactivation zone;
this is not the same as trying to attract all the charged particles
onto the surface of the plasma generator as in fact, such would be
undesirable as it could interfere with the effective operation of
the plasma generator if all the charged particles were on the
surface of the plasma generator.
[0109] The air treatment apparatus 2000 comprises a plasma
generator comprising the flexible electrode assembly 2101, which is
configured to operate at a power density less than 1 W/cm.sup.2 to
operably generate a plasma discharge. Most preferably, the plasma
generator is configured to be operated at a power density in the
range from 0.1 to 0.5 W/cm.sup.2. This is a relatively low power
density for plasma generation and is effective for creating an
inactivation zone about the plasma generator.
[0110] It is to be understood that combinations of the means for
inactivating the health threatening airborne pollutant materials
can be included in the air treatment apparatus of the present
invention; so that for instance, in an embodiment of the air
treatment apparatus, the plasma generating flexible electrode
assembly may be provided about at least a portion of the walls of
the cyclone geometry and a UV light may be included in the same
embodiment of the apparatus and/or an electrostatic precipitator
may also be provided in addition. Thus, the embodiments shown are
not to be taken as in isolation from each other but may be combined
so as to provide effective treatment of airflow.
[0111] Furthermore, at least two such air treatment apparatuses may
be provided in series so as to provide an array of air treatment
apparatuses with the outward airflow from a first air treatment
apparatus then being fed into a second air treatment apparatus as
the inward airflow for the second air treatment apparatus to ensure
efficient airflow treatment.
[0112] Referring now to FIG. 24, there is show yet a further
embodiment of the air treatment apparatus 2000A of the present
invention. As in the embodiments described in FIGS. 22 and 23, the
present embodiment includes the flexible electrode assembly 2101,
as previously described. However, in addition, the air treatment
apparatus 2000A of this embodiment further includes a UV light
source 1950 as previously described in the embodiments in FIGS. 20
and 21. Together, the flexible plasma assembly 2101 and the UV
light source create an effective inactivation zone for treatment of
airflow into the apparatus.
[0113] FIG. 25 shows the airflow pattern through an air treatment
apparatus such as 1101 or 1900, indicated by the arrows. FIG. 26 is
a graphical representation showing the air speed inside the cyclone
equivalent duct path with the air speeds in the sections A, B and C
shown in FIG. 25 respectively. The graphical representation shows
the increase as spike in the air speed in Zone B (FIG. 25) and the
plateau of the air speed in Zone C (FIG. 25). The changes in air
speed assist in enhancing the airflow through the apparatus and
within the inactivation zone for more efficient treatment of the
airflow. Referring to FIGS. 27 and 28, there is shown yet another
alternative embodiment of the air treatment apparatus 3000 of the
present disclosure. In this embodiment, the body 3002 of the air
treatment apparatus has a cylindrical shape, having an inner
ducting wall 3004 and an outer ducting wall 3006 and a closed end
3007. Incorporated within the apparatus 3000 is a UV light source
3008, which is positioned vertically and extending longitudinally
within the interior of the body 3002 of the apparatus. The inlet
air 3010 follows a circular airflow pathway 3012 between the outer
ducting wall 3006 and the inner ducting wall 3004, circulating
around the UV light source 3008, which creates an inactivation zone
for inactivating harmful pathogens and airborne particles within
the airflow. The circular airflow pathway 3012 travels from a top
3000a to the bottom 3000b of the apparatus 3000. FIG. 28 is a cross
sectional view of the air treatment apparatus 3000, showing the
circular airflow pathway 3012 through the device, between the outer
ducting wall 3006 and the inner ducting wall 3004 and the UV light
source 3008.
[0114] FIG. 29 is a cross sectional view of the air treatment
apparatus 3000 with the arrows showing the UV rays 3008a extending
from the UV light source 3008. Additionally, the inner wall of the
cylinder body is coated with a UV reflective layer 3009. The UV
reflective layer enhances the UV light rays 3008 such that the UV
light rays envelope the inside of the apparatus, creating the
inactivation zone within the interior of the air treatment
apparatus.
[0115] Referring now to FIG. 30, there is shown a further
alternative embodiment of the air treatment apparatus 4000 of the
present disclosure, similar to the embodiment in FIG. 29. In this
embodiment, the body 4002 of the air treatment apparatus 4000 is
also a cylindrical shape having the same diameter from top to
bottom and having a closed bottom 4007. However, the embodiment of
this apparatus 4000 incorporates a flexible electrode assembly
4006, specifically disposed on an inner surface 4003 of the body
4002 of the apparatus. As previously described in earlier
embodiments, the flexible electrode assembly 4006 is configured for
plasma generation thereby creating an inactivation zone within the
interior of the apparatus 4000 for receiving and treatment of
contaminated airflow as previously described.
[0116] Referring now to FIGS. 31a and 31b, there is shown yet
another embodiment of the air treatment apparatus 5000 of the
present disclosure. In this embodiment shown in FIG. 31a, the
apparatus 5000, having a generally cylindrical shape, incorporates
both a flexible electrode assembly 5002, disposed on the inner
surface of the apparatus, and a UV light source 5004 within the
interior of the apparatus. FIG. 31b is a cut-away sectional view of
FIG. 31a, showing more details of the UV light source 5004 within
the interior of the apparatus 5000. When used together, the
flexible electrode assembly 5002 disposed on an inner wall of the
apparatus, in combination with the UV light source 5004, create an
inactivation zone within the apparatus 5000 for treatment of
airflow containing various pollutants and contaminants, as the
airflow circulates through the apparatus as previously
described.
[0117] It will, of course, be understood, that various
modifications and alterations are possible within the scope of the
present invention, as defined in the appended claims.
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